| Literature DB >> 23077493 |
Jeremy C Andersen1, Nicholas J Mills.
Abstract
At the same time that molecular researchers are improving techniques to extract DNA from museum specimens, this increased demand for access to museum specimens has created tension between the need to preserve specimens for maintaining collections and morphological research and the desire to conduct molecular analyses. To address these concerns, we examined the suitability of non-invasive DNA extraction techniques on three species of parasitic Hymenoptera (Braconidae), and test the effects of body size (parasitoid species), age (time since collection), and DNA concentration from each extract on the probability of amplifying meaningful fragments of two commonly used genetic loci. We found that age was a significant factor for determining the probability of success for sequencing both 28S and COI fragments. While the size of the braconid parasitoids significantly affected the total amount of extracted DNA, neither size nor DNA concentration were significant factors for the amplification of either gene region. We also tested several primer combinations of various lengths, but were unable to amplify fragments longer than ~150 base pairs. These short fragments of 28S and COI were however sufficient for species identification, and for the discovery of within species genetic variation.Entities:
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Year: 2012 PMID: 23077493 PMCID: PMC3471897 DOI: 10.1371/journal.pone.0045549
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
Parasitoid specimens from the Essig Museum collection used for DNA extraction, indicating age, weight, extracted DNA concentration and success of sequencing the two selected genetic loci (together with base pair length).
| ID # | Location | Age (Years) | Collection Date | Weight (mg) | DNA (ng/ul) | 28S (bp) | COI (bp) |
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| J0075 | Yosemite, CA | 79 | 5.vi.1931 | 4.013 | 141.93 | No | No |
| J0076 | Fallen Leaf Lake, CA | 70 | 5.vii.1940 | 8.145 | 55.04 | Yes (140) | No |
| J0077 | Fallen Leaf Lake, CA | 70 | 5.vii.1940 | 3.763 | 44.58 | Yes (140) | No |
| J0078 | 6 mi east of Chester, CA | 56 | 14.vii.1954 | 5.273 | 113.53 | Yes (140) | No |
| J0079 | 6 mi east of Chester, CA | 56 | 14.vii.1954 | 5.011 | 66.08 | No | No |
| J0080 | 6 mi east of Chester, CA | 56 | 14.vii.1954 | 6.096 | 310.10 | No | No |
| J0081 | Hobart Mills, CA | 48 | 29.vii.1962 | 5.873 | 26.08 | Yes (140) | No |
| J0082 | 7 mi north of Truckee, CA | 48 | 29.vii.1962 | 2.584 | 63.36 | No | No |
| J0083 | 7 mi north of Truckee, CA | 48 | 29.vii.1962 | 2.780 | 115.70 | No | No |
| J0084 | 2 mi west of Brancomb, CA | 34 | 25–27.v.1976 | 3.225 | 84.28 | Yes (140) | No |
| J0085 | 2 mi west of Brancomb, CA | 34 | 25–27.v.1976 | 4.236 | 506.16 | Yes (140) | No |
| J0086 | 2 mi west of Brancomb, CA | 34 | 25–27.v.1976 | 2 | 74.00 | Yes (140) | Yes (103) |
| J0087 | Echo Lake, CA | 29 | 24.vi.1981 | 1.588 | 70.32 | Yes (140) | Yes (103) |
| J0088 | Echo Lake, CA | 29 | 24.vi.1981 | 1.739 | 113.22 | Yes (140) | Yes (103) |
| J0089 | Tahoe City, CA | 29 | 30.ix.1981 | 4.425 | 28.10 | Yes (140) | Yes (103) |
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| J0103 | Orono, ME | 96 | 27.vii.1914 | 0.161 | 13.70 | No | No |
| J0104 | Orono, ME | 96 | 27.vii.1914 | 0.256 | 152.82 | No | No |
| J0105 | Orono, ME | 96 | 26.vii.1914 | 0.295 | 5.90 | No | No |
| J0106 | La Jara Canyon, NM | 30 | 5.vii.1980 | 0.122 | 37.59 | Yes (139) | No |
| J0107 | La Jara Canyon, NM | 30 | 5.vii.1980 | 0.256 | 34.21 | Yes (139) | No |
| J0108 | La Jara Canyon, NM | 30 | 4.vii.1980 | 0.258 | 64.50 | Yes (139) | No |
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| J0109 | Santa Cruz, CA | 1 | 21.5.2009 | 0.198 | 78.95 | Yes (789) | Yes (658) |
| J0110 | San Francisco, CA | 1 | 3.vi.2009 | 0.274 | 51.05 | Yes (789) | Yes (658) |
| J0111 | San Francisco, CA | 1 | 17.vi.2009 | 0.220 | 31.40 | Yes (789) | Yes (658) |
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| J0090 | Rancho Santa Fe, CA | 51 | 18.viii.1959 |
| 11.10 | Yes (155) | Yes (128) |
| J0092 | Rancho Santa Fe, CA | 51 | 18.viii.1959 |
| 9.27 | No | No |
| J0093 | U.C. Insectary, Albany, CA | 47 | 2.v.1963 |
| 1.70 | Yes (155) | Yes (128) |
| J0094 | U.C. Insectary, Albany, CA | 47 | 2.v.1963 |
| 8.06 | Yes (155) | Yes (128) |
| J0095 | U.C. Insectary, Albany, CA | 47 | 2.v.1963 |
| 5.83 | No | No |
| J0096 | Citrus Exp. Station, Riverside, CA | 33 | 1977 |
| 1.30 | No | No |
| J0097 | Citrus Exp. Station, Riverside, CA | 33 | 1977 |
| 84.41 | No | Yes (128) |
| J0098 | Citrus Exp. Station, Riverside, CA | 33 | 1977 |
| 11.80 | No | No |
| J0099 | U.C. Insectary, Albany, CA | 17 | 13.vii.1993 | 0.006 | 4.80 | No | No |
| J0100 | U.C. Insectary, Albany, CA | 17 | 13.vii.1993 | 0.008 | 13.72 | Yes (155) | Yes (128) |
| J0101 | U.C. Insectary, Albany, CA | 17 | 13.vii.1993 | 0.014 | 11.00 | Yes (155) | Yes (128) |
| J0102 | Berkeley, CA | 17 | 4.viii.1993 | 0.023 | 593.84 | Yes (155) | Yes (128) |
Specimen weighed on mg scale.
Specimen could not be removed from mounting pin.
Figure 1Mean DNA concentrations from three braconid species.
Mean (±1 SE) DNA concentrations (ng/µl) extracted from three braconid species, as measured with a NanoDrop. Statistical differences between the species (p<0.05) are signified by a different letter above each column.
GLM model summaries for the probability of amplifying meaningful sequences of 28S and COI from three braconid parasitoid species.
| Model Description | K | AICc | Δ |
| Log-likelihood |
| 28S∼Age | 2 | 43.83 | 0 | 0.43 | −19.73 |
| 28S∼Age, Parasitoid species | 4 | 44.85 | 1.02 | 0.26 | −17.78 |
| 28S∼Age, log(DNA) | 3 | 45.09 | 1.26 | 0.23 | −19.17 |
| 28S∼Age, log(DNA), Parasitoid species | 5 | 47.47 | 3.64 | 0.07 | −17.73 |
| 28S∼log(DNA) | 2 | 51.53 | 7.7 | 0.01 | −23.58 |
| 28S∼Parasitoid species | 3 | 53.94 | 10.11 | 0 | −23.59 |
| 28S∼log(DNA), Parasitoid species | 4 | 56.19 | 12.36 | 0 | −23.45 |
| COI∼Age | 2 | 38.36 | 0 | 0.53 | −17 |
| COI∼Age, Parasitoid species | 4 | 39.98 | 1.62 | 0.24 | −15.34 |
| COI∼Age, log(DNA) | 3 | 40.64 | 2.28 | 0.17 | −16.94 |
| COI∼Age, log(DNA), Parasitoid species | 5 | 42.57 | 4.21 | 0.06 | −15.29 |
| COI∼Parasitoid species | 3 | 51.91 | 13.55 | 0 | −22.58 |
| COI∼log(DNA) | 2 | 52.45 | 14.09 | 0 | −24.04 |
| COI∼log(DNA), Parasitoid species | 4 | 53.16 | 14.8 | 0 | −21.94 |
Model names, descriptions, and AIC summaries for supported models examining factors contributing to the amplification of fragments of 28S and COI. K = the number of fitted parameters in the model, AICc = AIC score corrected for small sample sizes, Δ = the difference between the AICc of the current model and that of the model with the lowest AICc score, w = Akaike weights indicating the probability of the model being the correct model compared to all other tested models.
Model averaged estimates and uncertainty for the amplification of 28S and COI.
| 95% CI | ||||
| Parameter | Averaged parameter estimate | Weighted unconditional SE | Upper | Lower |
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| Intercept | 2.785 | 1.495 | 5.699 | −0.130 |
| Age | −0.054 | 0.022 |
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| log(DNA) | 0.198 | 0.329 | 0.840 | −0.444 |
| Parasitoid species ( | 0.186 | 1.407 | 2.929 | −2.557 |
| Parasitoid species ( | −1.740 | 1.035 | 0.278 | −3.757 |
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| Intercept | 2.840 | 1.470 | 5.707 | −0.026 |
| Age | −0.089 | 0.034 |
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| log(DNA) | −0.025 | 0.344 | 0.646 | −0.695 |
| Parasitoid species ( | −1.798 | 1.545 | 1.214 | −4.811 |
| Parasitoid species ( | 0.756 | 1.097 | 2.895 | −1.383 |
Model-averaged parameter estimates were calculated by averaging parameter estimates over all models in which a specific predictor was included. The new averaged parameter estimates are reported with standard errors (SE), as well as 95% confidence intervals (CI). Those parameters whose 95% CI did not include zero are highlighted in bold. Summaries for the categorical parameter Parasitoid species are reported relative to Parasitoid species (Atanycolus).
Figure 2Probability of amplifying fragments of 28S and COI.
The probability of successfully amplifying the 28S (left) and COI (right) gene fragments for specimens between 0 and 96 years old were estimated using the results from a logistic regression model with failure/success of amplification of each gene fragment as the response variable and age as the predictor variable. Circles represent the outcome for individual specimens, and the fitted curve from the logistic regression analysis is shown as a solid line, with associated 95% confidence intervals indicated by broken lines. For 28S the intercept equals 2.564±0.945 (t = 2.714, p = 0.01), with a slope of −0.049±0.02 (t = −2.463, p = 0.019), and for COI, the intercept equals 2.561±1.125 (t = 2.275, p = 0.023), with a slope of −0.081±0.03 (t = −2.689, p = 0.007).
Figure 3One of eight most parsimonious reconstructions of the 28S dataset.
Phylogram showing of one of the most parsimonious trees from the analysis of the 28S dataset. Bootstrap support values are shown either above or next to each supported branch. Sequences generated in this study are in bold. A scale bar indicating branch-lengths is shown in the bottom left.
Figure 4Examples of most parsimonious trees from the analyses of the COI datasets.
Phylograms showing of one of the most parsimonious trees from the analysis of the COI datasets for A) A. longifemoralis (one of 13 MP trees), B) Meteorus spp., (one of 10 MP trees) and C) T. pallidus (one of two MP trees). Bootstrap support values are shown either above or next to each supported branch. Sequences generated in this study are in bold. For each dataset, a scale bar indicating branch-lengths is shown in the bottom left.